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<br />I <br /> <br />I <br /> <br />I <br /> <br />Most of the irrigated soils are alluvial deposits of sandy loams <br />over coarse sands or gravelly sands underlain by shale at depths mostly <br />over 5 feet. Soils with shale at moderate depths occur in some areas. <br />Small areas of wind deposited sand dune soils and heavy clay soils also <br />occur. Also, soils shallow to shale bedrock occur in the surrounding <br />uplands. <br /> <br />I <br /> <br />I <br /> <br />The sandy loam soils are suitable for irrigation with some <br />limitations. The coarse texture results in low water holding capacity <br />and moderately rapid to rapid permeability. This generally leads to low <br />irrigation efficiencies under flood irrigation systems. The topography <br />is nearly level to gently sloping with some microrelief. Land smoothing <br />and leveling of this microrelief to facilitate more even distribution of <br />water under border dike or contour ditch irrigation methods removes the <br />topsoil from high spots and adds it to low areas. This increases soil <br />variability as to water holding capacity and productivity. <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />The low water holding capacity and moderately rapid to rapid <br />permeability of the soils results in much of the water from the canals, <br />ditches, and that applied to the field being lost through deep <br />percolation. This waste water is retained or held up as a perched water <br />table by the underlying shale. Buildup of a water table above the shale <br />has created wet soils conditions generally with accompanying salinity <br />and alkalinity. Drainage ditches have been installed to drain some <br />areas, but other areas would benefit if drainage were improved or deep <br />percolation reduced. Ditch lining and sprinkler irrigation should <br />reduce the extent of wet areas and lower the perched water table. This <br />could retard and even reduce the buildup of salinity and alkalinity. <br /> <br />I <br /> <br />I <br /> <br />I <br />I <br /> <br />Water erosion on the irrigated lands is generally not a problem as <br />the topography is nearly level to gently sloping, except for gullies <br />developing from waste water runoff and from water breaking out of <br />ditches. Wind erosion is a problem with a loamy fine sand, loamy sand, <br />or fine sand surface if these soils are left unprotected during the <br />critical wind erosion periods. <br /> <br />I <br /> <br />Fish and Wildlife Resources <br /> <br />I <br /> <br />Fisheries habitat is found on streams that flow throughout the <br />watershed area. Principal fish species present in the lower Big Sandy <br />River and Little Sandy Creek consist of rainbow and brown trout, carp, <br />and suckers. The lower Big Sandy River extends 40 miles from the town <br />of Farson to the confluence with the Green River. This reach of stream <br />is high in nutrients. It has fair to poor resident trout habitat <br />throughout. Major limiting factors for salmonids are excessive summer <br />temperature maximums and heavy accumulation of sediments. Populations <br />of trout are known to exist in this reach of the Big Sandy River when <br />temperature levels are acceptable, especially in the 8- to 10-mile <br />region of cold water bank seeps below Farson. Bone Draw is a left-side <br />tributary that empties into the Big Sandy River approximately 5 miles <br />below the project area. The water sources to Bone Draw are several <br />small cold water saline seeps that occur in the last one-half mile of <br />the draw. In addition, during the irrigation season, some intermittent <br />tail water runoff from the project area reaches the outlet of Bone Draw. <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />2-6 <br /> <br />OJ0&~9 <br />